JP2699666B2 - Deodorizing device - Google Patents
Deodorizing deviceInfo
- Publication number
- JP2699666B2 JP2699666B2 JP3011015A JP1101591A JP2699666B2 JP 2699666 B2 JP2699666 B2 JP 2699666B2 JP 3011015 A JP3011015 A JP 3011015A JP 1101591 A JP1101591 A JP 1101591A JP 2699666 B2 JP2699666 B2 JP 2699666B2
- Authority
- JP
- Japan
- Prior art keywords
- ozone
- catalyst
- malodorous components
- deodorizing
- layer
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Expired - Lifetime
Links
Landscapes
- Treating Waste Gases (AREA)
- Exhaust Gas Treatment By Means Of Catalyst (AREA)
- Solid-Sorbent Or Filter-Aiding Compositions (AREA)
Description
【0001】[0001]
【産業上の利用分野】本発明は、オゾンと触媒との組合
わせによって、悪臭成分を吸着捕集し、分解除去する脱
臭装置に関する。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a deodorizing apparatus for adsorbing and collecting malodorous components and decomposing and removing them by using a combination of ozone and a catalyst.
【0002】[0002]
【従来の技術】近年、悪臭公害が社会問題として大きく
取り上げられ、様々な新しい悪臭対策の技術が開発、実
施されている。2. Description of the Related Art In recent years, odor pollution has been widely taken up as a social problem, and various new odor control techniques have been developed and implemented.
【0003】従来、脱臭は薬剤洗浄法、吸着法、直燃
法、触媒燃焼法、オゾンによる酸化法などによって実施
されているが、それぞれ一長一短があり、実用上問題が
多い。たとえば前記のオゾンによる酸化法はオゾンの強
力な酸化作用を利用して悪臭成分を処理する方法で、室
温程度の低温でも処理できるため、前述した他の諸方法
に比べて、ランニングコストも安い方法である。しかし
ながら、オゾンと悪臭成分との気相中での反応が遅いた
めに長大な反応器を必要とし、また、未反応オゾンが排
出されるためオゾンによる二次公害が起こる欠点を有し
ている。Conventionally, deodorization has been carried out by a chemical cleaning method, an adsorption method, a direct combustion method, a catalytic combustion method, an oxidation method using ozone, etc., each of which has advantages and disadvantages, and has many practical problems. For example, the above-described oxidation method using ozone is a method of treating malodorous components by using the strong oxidation action of ozone, and can be treated even at a low temperature of about room temperature, so that the running cost is lower than the other methods described above. It is. However, there is a disadvantage that a long reactor is required because the reaction between the ozone and the malodorous component in the gas phase is slow, and secondary pollution by ozone occurs because unreacted ozone is discharged.
【0004】前述したような欠点を補う方法として2つ
の方法が提案されている。第1の方法は、オゾン発生器
とオゾン分解フィルタとを有した装置で脱臭する方法で
ある(特開昭61−29358号)。Two methods have been proposed as methods for compensating for the above-mentioned disadvantages. The first method is a method of deodorizing with an apparatus having an ozone generator and an ozone decomposition filter (Japanese Patent Application Laid-Open No. 61-29358).
【0005】この方法は未反応オゾンを分解させたのち
排気するため、二次公害の心配はなくなったものの、気
相中でオゾンと悪臭成分とを分解させるため反応器が大
容量となるか、あるいは反応器の容量が小さい場合、処
理ガスが充分脱臭されないうちにオゾン分解フィルタを
通過し、脱臭効果が小さくなる欠点を有している。In this method, unreacted ozone is decomposed and then exhausted, so that there is no fear of secondary pollution. However, it is necessary to increase the capacity of the reactor to decompose ozone and malodorous components in the gas phase. Alternatively, when the capacity of the reactor is small, the processing gas passes through the ozone decomposition filter before being sufficiently deodorized, and has a disadvantage that the deodorizing effect is reduced.
【0006】また、第2の方法はオゾンと悪臭成分とを
接触反応させ酸化反応を促進させると同時に、未反応の
オゾンをも接触分解させる目的で触媒を用いる方法であ
る。この方法に用いる触媒としては炭素質材質からなる
担体上に金属酸化物を担持させた触媒(特開昭54−1
19371号)、活性アルミナ担体に金属酸化物を担持
させた触媒(特開昭53−30908号)が開示されて
いる。しかし、いずれの触媒の場合とも、オゾン分解能
が高いため、所望の脱臭効果を得るためにはオゾンの消
費量が多く必要になる。The second method uses a catalyst for the purpose of contacting and reacting ozone with a malodorous component to promote an oxidation reaction and also to catalytically decompose unreacted ozone. As a catalyst used in this method, a catalyst in which a metal oxide is supported on a carrier made of a carbonaceous material (Japanese Patent Application Laid-Open No.
No. 19371) and a catalyst in which a metal oxide is supported on an activated alumina carrier (JP-A-53-30908). However, any of the catalysts has a high ozone decomposing ability, so that a large amount of ozone is required to obtain a desired deodorizing effect.
【0007】[0007]
【発明が解決しようとする課題】前述したように、従来
の技術では、悪臭成分を吸着捕集すると同時にオゾンを
分解するようなオゾン分解能の高い触媒を用いている。
このため、充分な脱臭効果を得るために、オゾンの消費
量が多くなるとともに、未反応オゾンの排出を実質的に
なくすことも困難である。As described above, in the prior art, a catalyst having a high ozone resolving power, which adsorbs and collects malodorous components and simultaneously decomposes ozone, is used.
For this reason, in order to obtain a sufficient deodorizing effect, the consumption of ozone is increased, and it is also difficult to substantially eliminate the emission of unreacted ozone.
【0008】本発明の目的は、オゾンの消費量を少なく
すると同時に充分な脱臭効果を得ることができる脱臭装
置を提供することである。[0008] It is an object of the present invention to provide a deodorizing apparatus capable of reducing ozone consumption and obtaining a sufficient deodorizing effect.
【0009】[0009]
【課題を解決するための手段】本発明は、オゾンと触媒
との組合わせによって、悪臭成分を吸着捕集し、分解除
去する脱臭装置において、前記脱臭装置はオゾンを分解
しにくくかつ悪臭成分を吸着する疎水性ゼオライトの吸
着層と、余分なオゾンを分解する触媒層とを含んで構成
されていることを特徴とする脱臭装置である。SUMMARY OF THE INVENTION The present invention relates to a deodorizing apparatus for adsorbing and collecting malodorous components by means of a combination of ozone and a catalyst to decompose and remove the malodorous components. A deodorizing device comprising an adsorbing layer of a hydrophobic zeolite to adsorb and a catalyst layer for decomposing excess ozone.
【0010】また本発明は、請求項1の脱臭装置におい
て吸着層と触媒層がハニカム構造であることを特徴とす
る。The present invention is also characterized in that the adsorption layer and the catalyst layer have a honeycomb structure in the deodorizing apparatus of the first aspect.
【0011】[0011]
【作用】本発明に従えば、まず悪臭成分を多く吸着捕集
でき、またオゾンを分解しにくい吸着層を用いて、悪臭
成分をオゾンと接触しながら酸化分解して無臭化する。
次に、オゾンを分解する触媒層に通し、余分なオゾンを
分解し無害化する。According to the present invention, first, a large amount of offensive odor components can be adsorbed and collected, and the odorous components are oxidized and decomposed while coming into contact with ozone by using an adsorption layer which does not easily decompose ozone, thereby eliminating odor.
Next, excess ozone is decomposed and made harmless through a catalyst layer that decomposes ozone.
【0012】オゾンと悪臭成分との酸化分解効果をよく
するために、吸着層はできるだけ悪臭成分の吸着量の大
きい、かつオゾンをできるだけ分解させないような材質
が好ましい。In order to improve the effect of oxidative decomposition of ozone and malodorous components, it is preferable that the adsorbing layer is made of a material which adsorbs as much malodorous components as possible and which does not decompose ozone as much as possible.
【0013】一般にゼオライトは、アンモニア、アミ
ン、メルカプタン等極性臭に対して、優れた吸着物質で
あることがよく知られている。しかし、ゼオライトは水
分吸着量が大きく、大気中で使用する場合、湿分の影響
によって悪臭成分の吸着捕集が妨げられ、実用上吸着量
が少なくなることが多い。In general, it is well known that zeolite is an excellent adsorbent for polar odors such as ammonia, amine and mercaptan. However, zeolite has a large amount of adsorbed moisture, and when used in the air, the influence of moisture hinders the adsorption and collection of malodorous components, and the amount of adsorbed zeolite often decreases in practical use.
【0014】これに対して、本発明の吸着層(図1にお
いて参照符号1で示す)で使用する疎水性ゼオライトは
化学的にはアルミノシリケート金属塩の結晶であり、そ
のシリカ構造中の酸素原子はほとんど塩基性を持たず、
水素結合の形成に関与しない。このため、ゼオライト表
面のSi−O−Si結合は撥水性を示し、水分子を吸着
しない。また、極性物質に対する強い吸着力は、骨格中
のアルミ原子数に対応するカチオンの静電力に依存する
ので、結晶中のAl2O3を減少し、SiO2/Al2O3
を大きくすれば撥水性が増大し、水分の吸着量を減少す
ることができる。On the other hand, the hydrophobic zeolite used in the adsorption layer of the present invention (indicated by reference numeral 1 in FIG. 1) is chemically a crystal of an aluminosilicate metal salt, and has oxygen atoms in its silica structure. Has almost no basicity,
Does not participate in hydrogen bond formation. For this reason, the Si—O—Si bond on the zeolite surface exhibits water repellency and does not adsorb water molecules. Further, since the strong adsorbing power to polar substances depends on the electrostatic force of the cation corresponding to the number of aluminum atoms in the skeleton, Al 2 O 3 in the crystal is reduced, and SiO 2 / Al 2 O 3
When is increased, the water repellency increases and the amount of adsorbed moisture can be reduced.
【0015】図2に示すように、水の吸着量はSiO2
/Al2O3が20の前後から低下し、80以上ではほと
んど水の吸着をしなくなる。一方、極性臭のアンモニ
ア、アミン、メルカプタンの吸着量はSiO2/Al2O
3が20〜80の範囲では大きく、特に40〜60の範
囲が好ましい。As shown in FIG. 2, the amount of water adsorbed is SiO 2
/ Al 2 O 3 decreases from around 20, and when it is 80 or more, almost no water is adsorbed. On the other hand, the adsorption amounts of ammonia, amine and mercaptan having polar odors are SiO 2 / Al 2 O
When 3 is in the range of 20 to 80, it is large, and particularly preferably in the range of 40 to 60.
【0016】さらにこの疎水性ゼオライトは吸着剤とし
て悪臭成分を多く吸着捕集すると同時に、オゾンの分解
には大きい影響を与えないという性質を持っている。Further, the hydrophobic zeolite has a property of adsorbing and trapping a large amount of malodorous components as an adsorbent, and at the same time, does not greatly affect the decomposition of ozone.
【0017】吸着効率の面から言うと、前記した疎水性
ゼオライトの構造は図1のようにハニカム(ハチの巣)
構造が好ましい。In terms of adsorption efficiency, the structure of the hydrophobic zeolite described above is a honeycomb (honeycomb) as shown in FIG.
The structure is preferred.
【0018】本発明の触媒層(図1において参照符号2
で示す)で使用される余分なオゾンを分解する触媒とし
ては通常のオゾン分解触媒が用いられる。たとえば、従
来のチタンおよびケイ素からなる二元系酸化物(以下T
iO2−SiO2と略称する)とβ型二酸化マンガン(以
下MnO2と略称する)とからなる触媒を使用してもよ
い。また、セラミック基材にTiO2−SiO2とMnO
2とを含浸させ、担持させてもよい。また、いずれの場
合もハニカム(ハチの巣)構造にすることが好ましい。The catalyst layer of the present invention (reference numeral 2 in FIG. 1)
As a catalyst for decomposing excess ozone used in the above, an ordinary ozone decomposition catalyst is used. For example, a conventional binary oxide composed of titanium and silicon (hereinafter referred to as T
A catalyst composed of iO 2 —SiO 2 ) and β-type manganese dioxide (hereinafter abbreviated as MnO 2 ) may be used. In addition, TiO 2 —SiO 2 and MnO
2 may be impregnated and carried. In any case, it is preferable to have a honeycomb (honeycomb) structure.
【0019】なお上記した吸着層と触媒層とは一体化し
てもよいが、別々に設けてもよい。The above-mentioned adsorption layer and catalyst layer may be integrated, or may be provided separately.
【0020】前記したような吸着層と触媒層を用いて、
悪臭成分を分解すると、以下の実施例に示すようにオゾ
ン消費量を明らかに低減することができる。Using the adsorption layer and the catalyst layer as described above,
Decomposing the malodorous components can significantly reduce ozone consumption, as shown in the examples below.
【0021】[0021]
【実施例】20℃、60%室内湿度の空気中で、0.2
mg/m3濃度の極性臭ジメチルアミンを従来技術の装
置と本発明との装置で脱臭処理し、その結果を比較し
た。従来技術たとえばマンガン触媒を用いて直接処理す
る場合には、臭気が感知できなくなる(0.1PPM以
下)まで処理するためのオゾン消費量は0.8mg/m
3であった。EXAMPLE In an air at 20 ° C. and 60% room humidity, 0.2
The polar odor dimethylamine having a concentration of mg / m 3 was subjected to a deodorizing treatment using the conventional apparatus and the present invention, and the results were compared. In the prior art, for example, in the case of direct treatment using a manganese catalyst, the amount of ozone consumed for treatment until the odor becomes undetectable (0.1 PPM or less) is 0.8 mg / m 2.
Was 3 .
【0022】一方、同じ条件で本発明の装置で脱臭すれ
ば、オゾン消費量は0.3mg/m3であった。On the other hand, when deodorization was carried out with the apparatus of the present invention under the same conditions, the ozone consumption was 0.3 mg / m 3 .
【0023】以上の比較実験の結果から明らかなよう
に、本発明によれば悪臭成分を酸化分解するのに消費さ
れるオゾンの量を低減することができる。As is clear from the results of the above comparative experiments, according to the present invention, the amount of ozone consumed for oxidatively decomposing malodorous components can be reduced.
【0024】[0024]
【発明の効果】本発明によれば、吸着層と触媒層がそれ
ぞれ悪臭成分の吸着捕集と余分な有害なオゾンの分解と
をすることによって、充分な脱臭効果を得ることができ
る。また、未反応のオゾンを分解させたのち排気するた
め、二次公害の心配はなくなると同時に、特にオゾンの
消費量を低減することができる。According to the present invention, a sufficient deodorizing effect can be obtained by the adsorption layer and the catalyst layer absorbing and collecting malodorous components and decomposing excess harmful ozone, respectively. In addition, since unreacted ozone is decomposed and then exhausted, there is no need to worry about secondary pollution, and the ozone consumption can be particularly reduced.
【図1】本発明による脱臭装置の簡略化した斜視図であ
る。FIG. 1 is a simplified perspective view of a deodorizing device according to the present invention.
【図2】疎水性ゼオライトのSiO2/Al2O3に対す
る水吸着量と悪臭(20℃、60%室内湿度中の10p
pmアンモニア)吸着量を示すグラフである。FIG. 2 Amount of water adsorbed on SiO 2 / Al 2 O 3 of a hydrophobic zeolite and bad odor (10 p at 20 ° C., 60% room humidity)
4 is a graph showing the amount of pm ammonia adsorbed.
1 吸着層 2 触媒層 1 adsorption layer 2 catalyst layer
Claims (2)
臭成分を吸着捕集し、分解除去する脱臭装置において、
前記脱臭装置はオゾンを分解しにくくかつ悪臭成分を吸
着する疎水性ゼオライトの吸着層と、余分なオゾンを分
解する触媒層とを含んで構成されていることを特徴とす
る脱臭装置。1. A deodorizing device for adsorbing and collecting malodorous components and decomposing and removing them by a combination of ozone and a catalyst.
The deodorizing apparatus is characterized in that the deodorizing apparatus includes a hydrophobic zeolite adsorption layer that is less likely to decompose ozone and adsorbs malodorous components, and a catalyst layer that decomposes excess ozone.
媒層がハニカム構造であることを特徴とする脱臭装置。2. The deodorizing apparatus according to claim 1, wherein the adsorption layer and the catalyst layer have a honeycomb structure.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP3011015A JP2699666B2 (en) | 1991-01-31 | 1991-01-31 | Deodorizing device |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP3011015A JP2699666B2 (en) | 1991-01-31 | 1991-01-31 | Deodorizing device |
Publications (2)
Publication Number | Publication Date |
---|---|
JPH04313320A JPH04313320A (en) | 1992-11-05 |
JP2699666B2 true JP2699666B2 (en) | 1998-01-19 |
Family
ID=11766290
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP3011015A Expired - Lifetime JP2699666B2 (en) | 1991-01-31 | 1991-01-31 | Deodorizing device |
Country Status (1)
Country | Link |
---|---|
JP (1) | JP2699666B2 (en) |
Families Citing this family (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH06190236A (en) * | 1992-12-24 | 1994-07-12 | Ebara Infilco Co Ltd | Method of purifying gas and device therefor |
JP3126012B2 (en) * | 1994-08-31 | 2001-01-22 | ニチアス株式会社 | How to Prevent Odor Generation from Ozone Filter |
Family Cites Families (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS58124524A (en) * | 1982-01-21 | 1983-07-25 | Mitsubishi Heavy Ind Ltd | Removal of malodorous component |
-
1991
- 1991-01-31 JP JP3011015A patent/JP2699666B2/en not_active Expired - Lifetime
Also Published As
Publication number | Publication date |
---|---|
JPH04313320A (en) | 1992-11-05 |
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